Reservoir Sediment Carbon along the Elwha River after Removal of Dams

Backed by Scienceluv, Bob Appel, and Cindy Wu
$95
Raised of $5,000 Goal
2%
Ended on 6/17/13
Campaign Ended
  • $95
    pledged
  • 2%
    funded
  • Finished
    on 6/17/13

About This Project

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What is the context of this research?

The recent removal of two dams on the Elwha River provides a unique opportunity to assess the sediments remaining after the dam removal. Worldwide, numerous dams are aging and will either need to be replaced or removed within the next few decades. However, little is understood about the fate of the carbon stored in the sediments when a dam is removed.

This proposal assesses the pool of carbon in the sediments of the former Lake Mills and Lake Aldwell. Estimates of carbon storage would be mapped spatially and by depth. Additionally, gaseous carbon fluxes to the atmosphere would be measured to provide a preliminary estimate of respiration losses. This dam removal project, the largest-known of its kind, can provide important information regarding the fate of carbon in sediment pools and fluxes when reservoir sediments become soil.

What is the significance of this project?

The sample collection, mapping and quantification of carbon in the reservoir sediments will provide Olympic National Park with information regarding carbon stored there, and allowing modeling of potential carbon losses as well as future carbon sequestration. This project also has significance beyond that of the Elwha River. As other dam removal projects are considered this project would provide key information regarding pools of carbon after reservoir sediments are exposed. Additionally, experiments done to assess loss of C to the atmosphere could tell us about possible fluxes of greenhouse gases which could be compared to future photosynthetic inputs.

What are the goals of the project?

With completion of the Elwha River dam removal, the remaining reservoir sediments are exposed and accessible. Some areas of the sediments have already been planted as part of restoration efforts by ONP (Olympic National Park). The surficial sediments are easily accessible for sampling by roads and trails. Sampling of deeper sediments will be more challenging. After acquiring a research permit from ONP, we will finalize sampling protocols and coordinate sampling with Dr. Steve Acker, a plant ecologist with ONP and Josh Chenoweth, coordinator of the restoration activities at the Elwha River.

Budget

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Salaries and Wages for help with work on coring, carbon analysis, and technical services: 76% Travel: 17% Supplies and Materials: 7%

Meet the Team

Seth Wing
Seth Wing
M.S. Candidate

Affiliates

2011 - BA, UCLA, Geography/Environmental Studies, GIS
2014 - MS, University of Washington, Forest and Environmental Sciences
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Team Bio

My research background has been in soil and sediment carbon sequestration and biomass distribution. Previously I have concentrated in arid environments of Southern Africa and the Western United States. However, being in Washington, the surrounding environment makes for a fantastic natural lab, thus allowing me to shift my interests to a more temperate setting with an incredible array of biogeochemical diversity.

Seth Wing

My research background has been in soil and sediment carbon sequestration and biomass distribution. Previously I have concentrated in arid environments of Southern Africa and the Western United States. However, being in Washington, the surrounding environment makes for a fantastic natural lab, thus allowing me to shift my interests to a more temperate setting with an incredible array of biogeochemical diversity.

Additional Information

Sample collection sites will be set up using a grid system within sections to ensure spacing of sampling. Within each section, grid points will be randomly chosen for sampling. At least 30 surficial sampling sites will be chosen. Surficial sampling will be done by digging small holes that are 50-100cm deep, and then coring from 1m to 2 m. Samples will be collected from 0- 25cm, 25-50cm, 50-100cm, 100-150cm, and 150-200cm. In areas where the soil is coarse textured (cobbles and gravel), samples will be collected using pits to as close as 2 m deep as possible. Soil bulk density samples will also be collected while collecting samples for carbon analysis.

Access to deeper sediments is more difficult as deep coring is not feasible. Sampling will be done by accessing sideslopes that are open and accessible from the eroded sediments. At least 20 locations will be chosen for deep sampling. At these sites, samples will be collected from the sideslope every 1m after the top 2 meters to the deepest possible depth. Samples will also be collected for bulk density.

Carbon is also stored in coarse woody debris in the reservoir, namely with logs. Carbon stored in woody debris will be measured by first estimating the volume of the log using diameter and length measures and taking samples of the wood for analyses. C analysis will be done on all samples following drying using a CHN analyzer (Perkin-Elmer). While it is most likely that all of the carbon in the sediments is organic carbon, samples will be tested to determine if any carbonate carbon is present. If carbonates are found, these will be measured separately by analyzing samples before and after treatment to remove carbonates.

Sediment samples will be analyzed through a geographic information system (GIS) to better understand the organic carbon distribution through vertical and horizontal space in a reservoir setting. This will primarily involve the use of interpolation statistics to visualize carbon concentration within a spatial context. Sample sites will be assigned x, y coordinates and will also be given a Z value which will represent carbon content. For each core, coordinate will be taken using a high-accuracy GPS device which will allow for accurate mapping of samples. Once all data is collected and input, kriging—a common geostatistical interpolation tool—will be used within ESRI’s ArcGIS 10.1 software package. This technique will be utilized for its power to calculate values between sample points when distance and direction are assumed to reflect spatial correlation. This information, in turn, can be used to explain variation in the surface from one known point to the next, thus producing a comprehensive sediment carbon map of the drained reservoir at differing depths.

In addition to mapping carbon, we will estimate the total carbon stored in the sediments using the concentrations, depth measurements, grid area and bulk densities. This total storage of carbon in the sediment pool will be a unique measure that can be used to estimate future carbon transfer to the ocean by erosion, and can serve as a baseline to measure other carbon fluxes.

One carbon flux from the reservoir sediments that could be significant is gaseous losses of carbon. We propose to do some preliminary sampling of gaseous losses of carbon from the sediments. Twelve small rings will be pounded into the sediments at locations that cannot be easily accessed by the public so that rings can remain in place. Each ring will be sealed along the outer edge. Sleeves will fitted over these rings that can also be sealed using putty. A flat plexiglass plate containing a septum will be attached to the top of the sleeve to form a cylindrical chamber. These chambers will be places on the rings for a 24 hr period once a month. Samples will be collected at the end of the 24 hr period using a gas tight syringe and returned to the lab for analysis using a gas chromatograph. With a know time period, specific chamber volume, soil surface area, and concentration of gas, the flux of gas from the soil can be determined. This preliminary data will be used to estimate the relative importance of gaseous losses of carbon. Possible future work could examine the accumulation of carbon within the soil/sediments and the accumulation of carbon in vegetation.

Project Backers

  • 3Backers
  • 2%Funded
  • $95Total Donations
  • $31.67Average Donation
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